首页> 外文会议>9th International Conference on Environmental Remediation and Radioactive Waste Management >RADIOACTIVE WASTE EVAPORATION: CURRENT METHODOLOGIES EMPLOYED FOR THE DEVELOPMENT, DESIGN AND OPERATION OF WASTE EVAPORATORS AT THE SAVANNAH RIVER SITE AND HANFORD WASTE TREATMENT PLANT
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RADIOACTIVE WASTE EVAPORATION: CURRENT METHODOLOGIES EMPLOYED FOR THE DEVELOPMENT, DESIGN AND OPERATION OF WASTE EVAPORATORS AT THE SAVANNAH RIVER SITE AND HANFORD WASTE TREATMENT PLANT

机译:放射性废物蒸发:萨凡纳河站点和汉福德废物处理厂开发,设计和运行废物蒸发器的现行方法

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Evaporation of High Level and Low Activity (HLW & LAW) radioactive wastes for the purposes of radionuclide separation and volume reduction has been conducted at the Savannah River and Hanford Sites for more than forty years. Additionally, the Savannah River Site (SRS) has used evaporators in preparing HLW for immobilization into a borosilicate glass matrix. The Hanford River Protection Project (RPP) is in the process of building the world's largest radioactive waste treatment facility, Waste Treatment Plant (WTP), which will use evaporators to concentrate the liquid waste and plant recycles prior to immobilization into a borosilicate glass matrix. Radioactive waste is evaporated at each site using various evaporator designs (e.g., forced circulation, horizontal bent tube). While the equipment used to evaporate radioactive waste is relatively simple in design, the complexity in the evaporator processes in current service and in those currently in the design stages stems from the heterogeneous nature of the waste and the effects of seemingly minor components (e.g., Si) on the process. Aqueous electrolyte thermodynamic modeling and experiments have been conducted by the SRS Savannah River Technology Center (SRTC) in support of the SRS HLW and Defense Waste Processing Facility (DWPF) Evaporators and the Hanford RPP WTP. After 40 years of successful operation, accumulation of two solid phases (a nitrated aluminosilicate, Na_8Al_6Si_6O_(24)(NO_3)_2·4H_2O and sodium diuranate, Na_2U_2O_7) developed as an insoluble phase in the Savannah River Site (SRS) 2H evaporator in 1996. The aluminosilicate scale deposit caused the SRS 2-H evaporator to become completely inoperable by October 1999. Accumulation of the sodium diuranate phase on the aluminosilicate scale has caused criticality concerns. Modeling and experiments were conducted to develop a method to control the process chemistry in order to prevent the formation of aluminosilicate deposits in the future. The lessons learned from the development, design, and operation of the SRS waste treatment facilities and the currently operating 242-A Hanford HLW evaporators were applied by SRTC in support of the development and design of the Hanford WTP evaporators. Thermodynamic equilibrium modeling along with solubility and physical property experiments are being conducted to develop process control and flow sheet models. Additionally, lessons learned from the development of an advanced antifoam agent for the SRS vitrification process evaporators are being applied to the testing and development of an antifoam agent for the Hanford WTP evaporators. This paper will discuss the methodologies, results, and achievements of the SRTC evaporator development program that was conducted in support of the SRS and Hanford WTP evaporator processes. The "cross-pollination" and application of waste treatment technologies and methods between the Savannah River and Hanford Sites will be highlighted. The "cross-pollination" of technologies and methods is expected to benefit the Department of Energy's Mission Acceleration efforts by reducing the overall cost and time for the development of the baseline waste treatment processes.
机译:在萨凡纳河和汉福德场址进行了高放射性和低放射性(HLW和LAW)放射性废物的蒸发,目的是分离和减少放射性核素。此外,萨凡纳河工地(SRS)已使用蒸发器来制备可固定在硼硅酸盐玻璃基体中的HLW。汉福德河保护项目(RPP)正在建设世界上最大的放射性废物处理设施废物处理厂(WTP),该设施将使用蒸发器浓缩液体废物,并在固定到硼硅酸盐玻璃基体之前进行工厂循环利用。使用各种蒸发器设计(例如,强制循环,水平弯管)在每个站点蒸发放射性废物。虽然用于蒸发放射性废物的设备的设计相对简单,但是当前使用的蒸发器过程和当前处于设计阶段的蒸发器过程的复杂性源于废物的异质性和看似很小的成分(例如Si)的影响。 )。 SRS萨凡纳河技术中心(SRTC)已进行了水电解质热力学建模和实验,以支持SRS HLW和国防废物处理设施(DWPF)蒸发器以及Hanford RPP WTP。经过40年的成功运营,1996年在萨凡纳河站点(SRS)2H蒸发器中形成了两个固相(硝化的铝硅酸盐Na_8Al_6Si_6O_(24)(NO_3)_2·4H_2O和重铁酸钠Na_2U_2O_7)的累积,成为不溶相。铝硅酸盐水垢沉积物导致SRS 2-H蒸发器在1999年10月之前完全无法使用。进行建模和实验以开发一种控制过程化学的方法,以防止将来形成铝硅酸盐沉积物。 SRTC从SRS废物处理设施的开发,设计和运行以及当前运行的242-A Hanford HLW蒸发器中学到的经验教训被SRTC用来支持Hanford WTP蒸发器的开发和设计。进行热力学平衡建模以及溶解度和物理性质实验,以开发过程控制和流程图模型。此外,从用于SRS玻璃化工艺蒸发器的高级消泡剂的开发中汲取的经验教训已被用于汉福德WTP蒸发器的消泡剂的测试和开发。本文将讨论为支持SRS和Hanford WTP蒸发器工艺而进行的SRTC蒸发器开发程序的方法,结果和成就。萨凡纳河和汉福德遗址之间的“异花授粉”和废物处理技术和方法的应用将被重点介绍。技术和方法的“异花授粉”有望通过减少开发基准废物处理流程的总体成本和时间,使能源部的任务加速工作受益。

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